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ISSN 0097-8078, Water Resources, 2018, Vol. 45, No. 2, pp. 222–230. © Pleiades Publishing, Ltd., 2018.
Original Russian Text © V.N. Egorov, S.B. Gulin, L.V. Malakhova, N.Yu. Mirzoeva, V.N. Popovichev, N.N. Tereshchenko, G.E. Lazorenko, O.V. Plotitsina, T.V. Malakhova,
V.Yu. Proskurnin, I.G. Sidorov, A.P. Stetsyuk, L.V. Gulina, 2018, published in Vodnye Resursy, 2018, Vol. 45, No. 2.
Rating Water Quality in Sevastopol Bay by the Fluxes
of Pollutant Deposition in Bottom Sediments
V. N. Egorov*, S. B. Gulin, L. V. Malakhova, N. Yu. Mirzoeva, V. N. Popovichev, N. N. Tereshchenko,
G. E. Lazorenko, O. V. Plotitsina, T. V. Malakhova, V. Yu. Proskurnin, I. G. Sidorov,
A. P. Stetsyuk, and L. V. Gulina
Kovalevskii Institute of Marine Biological Research, Sevastopol, 299011 Russia
*e-mail: egorov.ibss@yandex.ru
Received May 13, 2015; in final form, January 26, 2017
Abstract⎯Sevastopol Bay is used as an example for the development of criteria for rating anthropogenic
impact by elimination fluxes from the water area of post-Chernobyl (
90
Sr,
137
Cs,
239,240
Pu) and natural (
210
Pо)
radionuclides, as well as mercury and organochlorine compounds. The differentiation of the bay water area
into zones with different biogeochemical conditions and the balance approach to interpreting field observa-
tion data were used to assess the conditioning capacity of Sevastopol Bay ecosystem for conservative radioac-
tive and chemical substances by elimination fluxes of pollutants into aqueous depot, which is the open part
of the Black Sea and into the geological depot, i.e., its bottom sediment stratum.
Keywords: Sevastopol Bay, bottom sediments, post-Chernobyl radionuclides, mercury, organochlorine com-
pounds, deposition fluxes
DOI: 10.1134/S0097807818020069
INTRODUCTION
Sevastopol Bay is a water area of higher environ-
mental risk because of its limited water exchange with
outer harbor resulting from the construction of pro-
tection piers, high technogenic activity in the coastal
area, wastewater discharges [9], and pollutant inputs
with the Chernaya R. water [8]. The need to control
the ecological state of the bay requires the regulation
of the equilibrium between the use and reproduction
of the quality of its water resources.
The objective of the study was to develop criteria
for rating the anthropogenic impact on Sevastopol
Bay water area by the deposition fluxes into its bottom
sediment of post-Chernobyl (
90
Sr,
137
Cs, and
239,240
Pu)
and natural (
210
Po) radionuclides, as well as mercury
and chlorinated hydrocarbons under current condi-
tions of natural biogeochemical cycles, through which
its water conditioning is taking place.
MATERIALS AND METHODS
The study was carried out in Sevastopol Bay and,
for comparison, in the outer harbor of Sevastopol. The
zoning of the bay water area by hydrodynamic, hydro-
chemical, and morphological characteristics (Fig. 1)
has been carried out in accordance with criteria
described in [5, 11]. The concentrations of
90
Sr,
137
Cs,
239,240
Pu,
210
Po, Hg and organochlorine compounds
(OCC) were measured by standard procedures [6, 10,
12]. To date the bottom sediments in the study areas,
soil core columns were taken and separated into layers
5–10 mm in thickness; the concentrations of
137
Cs or
90
Sr were measured in each layer, depending on which
radiotracer has been chosen. The data samples thus
obtained were compared to identify layers with maxi-
mal radionuclide concentrations. The formation age
of these layers corresponded to periods of maximal
fallout of fission radionuclides after global nuclear
weapon tests in the atmosphere, on land surface, and
in oceans in 1962, as well as the result of the release of
post-Chernobyl radionuclides into the environment in
1986. The rate of sedimentation was evaluated by the
distance between layers with peak concentration val-
ues of fission radionuclides both between one another
and from the surface layer in the core columns. A cor-
rection was introduced to account for changes in soil
density in bottom sediment columns [1, 3, 7].
RESULTS AND DISCUSSION
The radioactive and chemical substances under
consideration are conservative pollutants of the
marine environment. Therefore, the main self-purifi-
cation mechanisms of the marine environment involve
only the reduction of their concentrations in water
because of their migration into nearby water areas and
sedimentation elimination into bottom sediments.
HYDROCHEMISTRY, HYDROBIOLOGY, ENVIRONMENTAL ASPECTS